Tailor Pomatomus saltatrix

Lenore Litherlanda, James Andrewsb, Paul Lewisc and John Stewartd


Tailor

Table 1: Stock status determination for Tailor

Jurisdiction

Queensland, New South Wales, Victoria

Western Australia

Stock

Eastern Australian

(CIF, ECIFFF, EGF, GLF, OHF, OPSF, OTLF, PPBF)

Western Australian

(EF, GDSMF, OA, SBBSMNMF, SCEMF, WCDGDLIMF, WCDSIMF, WCEIMF)

Stock status

   

Sustainable

Sustainable

Indicators

Biomass, catch, effort, fishery-dependent length and age frequency, estimates of total mortality rate

Catch, juvenile index


CIF = Corner Inlet Fishery (Victoria); ECIFFF = East Coast Inshore Fin Fish Fishery (Queensland); EF = Estuaries Fisheries (Condition) (Western Australia); EGF = Estuary General Fishery (New South Wales); GDSMF = Gascoyne Demersal Scalefish Managed Fishery (Western Australia); GLF = Gippsland Lakes Fishery (Victoria); OA = Open Access (Western Australia); OHF = Ocean Haul Fishery (New South Wales); OPSF = Ocean Purse Seine Fishery (Victoria); OTLF = Ocean Trap and Line Fishery (New South Wales); PPBF = Port Phillip Bay Fishery (Victoria); SBBSMNMF = Shark Bay Beach Seine and Mesh Net Managed Fishery (Western Australia); SCEMF = South Coast Estuarine Managed Fishery (Western Australia); WCDGDLIMF = West Coast Demersal Gillnet and Demersal Longline (Interim) Managed Fishery (Western Australia); WCDSIMF = West Coast Demersal Scalefish (Interim) Managed Fishery (Western Australia); WCEIMF = West Coast Estuarine (Interim) Managed Fishery (Western Australia)


Stock Structure

Genetic evidence indicates that there are two biological stocks of Tailor in Australia, one along the east coast and a second along the west coast 1. The eastern Australian biological stock is distributed from Bundaberg in southern Queensland along the entire New South Wales coast and into eastern Bass Strait in Victoria2. The western Australian biological stock is distributed along the western coastline of Australia from Exmouth to Esperance3,4. Within each stock, multiple spawning groups may exist that spawn at different times and locations2,5,6. However, several characteristics, such as the dispersal of pelagic eggs and larvae with prevailing currents, the movement of juveniles into sheltered near-shore or estuarine habitats in northern and southern areas of the species range, and the seasonal migration behaviour of adults, suggest that a genetically homogenous population occurs on each coast2,3,5–7. The status for Tailor is reported here at the level of the two individual biological stocks.


Stock Status

Eastern Australian biological stock 

Tailor is commonly fished throughout its distribution along the east coast of Australia. Queensland, New South Wales and Victoria each assess that part of the biological stock that occurs in their waters. The status presented here for the entire biological stock has been established using evidence from all three jurisdictions.

Tailor has a long history as a key fishery species for Indigenous, commercial and recreational fishers. Since the 1970s, the eastern Australian biological stock of Tailor has predominantly been targeted by the recreational fishery8. The most recent stock assessment8,9 indicated that the total recreational and commercial harvest of Tailor from Queensland and New South Wales peaked in the mid-1970s and again in the mid-1990s. These peaks coincided with periods of high recruitment to the fishery, when favourable environmental factors allowed larger numbers of young Tailor to thrive 8. Since 2001, recruitment has been considered to be below average8. When assessed in 2008, the combined Queensland and New South Wales component of the stock was above 50 per cent of virgin biomass, and the total harvest was below the estimated maximum sustainable yield (MSY) of 1326 tonnes (t)8,10. Since 2008, the commercial (Queensland and New South Wales) and recreational (Queensland) harvest of Tailor has decreased 10,11, suggesting that the total harvest has remained below MSY.

In Queensland, commercial landings and catch rates have decreased since 2010, reaching historically low levels in 2013. The decline reflects particularly low harvest from beach-seine netting following changes in management arrangements that have resulted in reduced nominal effort10. Fishery-dependent monitoring of length and age indicates a stable size composition of fish, and shows that older fish (4–7-year-olds) are present in the harvest. These are positive indicators of a stable population with continued recruitment. Fishery-dependent monitoring between 1999 and 2013 found no fish approaching the species’ maximum age of 1310. On the whole, the data indicate that the biomass of the Queensland part of the stock is unlikely to be recruitment overfished.

In Queensland, management measures progressively introduced since 2002 have been effective in lowering fishing pressure10. Nominal effort in the commercial fishery in 2013 is the lowest in 5 years10. Recreational harvest estimates in 2011 were around one-third of the estimate in 2001, and there has been a reduction in the participation rate by recreational fishers in areas where Tailor are most commonly caught11. The minimum legal size (35 cm total length) is set above the size at maturity12, which reduces fishing pressure on the spawning stock and ensures that mature fish can spawn at least once. A seasonal closure also provides some protection of fish during the spawning period. Fishery-dependent age-frequency information shows evidence of continued recruitment, with 2–5-year-olds dominating the harvest10. Estimates of the total mortality rate from 2007 to 2013 are high, but are considered to be within an acceptable range for this species10. The data indicate that the current level of fishing pressure is unlikely to cause the Queensland component of the stock to become recruitment overfished.

In New South Wales, the length composition in commercial landings has remained consistent, typically ranging between 30 and 45 cm fork length. Nominal commercial catch rates (kilograms per day of line fishing) have increased steadily since the late 1990s. This evidence indicates that the biomass of the New South Wales part of the stock is unlikely to be recruitment overfished.

In New South Wales, the minimum legal size (30 cm total length) corresponds to the size at maturity. The recreational fishery is subject to the minimum legal length and a possession limit of 20 fish per person, which may do little to constrain harvest in this fishery sector. No recent estimate of the recreational harvest in New South Wales is available; historically, it has been substantially greater than the commercial harvest8,13. Therefore, fishing pressure from the recreational sector could be high. Fishing pressure is considered adequately controlled in the commercial fishery through restrictive daily trip limits of 100 kg per day (ocean haul nets) or 50 kg per day (other netting methods). As a result, commercial landings have been relatively stable since the early 2000s. On the whole, the evidence indicates that the current level of fishing pressure is unlikely to cause the New South Wales component of the stock to become recruitment overfished.

In Victoria, most of the commercial catch of Tailor since 2007 has come from the Gippsland Lakes14. The most recent assessment15 for Tailor in the Gippsland Lakes used the commercial mesh-net catch rate (kg/km-lift) as an indicator. Despite a decrease in the 5-year moving average (11.06 kg/km-lift), the indicator in 2010 was above the long-term average (based on a 32-year time series of data), indicating that there was no evidence of a long-term decline. This indicates that the biomass of the Victorian part of the stock is unlikely to be recruitment overfished.

In Victoria, the minimum legal size (23 cm total length) is below the size at maturity. The recreational fishery is subject to the minimum legal length and a bag/possession limit of 20 fish per person. Although there is no recent estimate of the recreational harvest of Tailor in Victoria, historically it was much less than in Queensland and New South Wales10,16. Commercial landings show minor fluctuations since the early 2000s10, and the total catch in 2013 of 39.6 t was the second highest in 10 years. This indicates that fishing pressure is unlikely to cause the Victorian component of the stock to become recruitment overfished.

On the basis of the evidence provided above, the entire biological stock is classified as a sustainable stock.  

Western Australian biological stock 

The western Australian biological stock is accessed by one jurisdiction, Western Australia. Similar to the east coast, Tailor is predominantly a recreational species in Western Australia, with approximately 85 per cent taken by shore-based fishers4,17. In the 1990s, there was a marked decline in size and numbers of Tailor caught along the west coast. Since then, management measures have been introduced4. The most recent stock assessment4 (2013) for the western Australian biological stock of Tailor used a weight-of-evidence approach. The assessment indicated that the stock had a low inherent vulnerability, and catch rates suggested that the current spawning stock abundance is high4. Annual recruitment by juvenile Tailor has been monitored in the Perth metropolitan area since 1996, and results suggest increasing recruitment since 2006. Increasing recreational catch rates of adult Tailor throughout the West Coast Bioregion in recent years are consistent with higher recruitment across the entire biological stock. Since 2001, the annual harvest and catch rates of Tailor in the main commercial fisheries (Shark Bay Beach Seine and Mesh Net Managed Fishery, and West Coast Estuarine [Interim] Managed Fishery) have been stable (combined 24–35 t) and are considered adequate, even though the Shark Bay Beach Seine and Mesh Net Managed Fishery catch is below the historical range as a result of local processing restrictions4,18.The above evidence indicates that the biomass of the stock is unlikely to be recruitment overfished.

Management changes implemented in Western Australia between 1990 and 2009 (bag and size limits) have been effective in reducing the retained recreational harvest of Tailor. Although the current minimum legal size (30 cm total length) is just below the size at maturity, the maximum size possession limit (only two fish over 50 cm total length in the West Coast Bioregion) ensures protection for the breeding stock, and no additional management actions are expected to be implemented. The most recent stock assessment estimated a moderately high rate of natural mortality. However, the biological characteristics of fast growth rate and early maturity imply a low vulnerability of the stock to exploitation4. The above evidence indicates that the current level of fishing pressure is unlikely to cause the stock to become recruitment overfished.

On the basis of the evidence provided above, the biological stock is classified as a sustainable stock.


Table 2: Tailor biology4,5,7,10,12

Longevity and maximum size

11–13 years; 1200 mm TL

Maturity

Eastern Australian biological stock:1–2 years; males 290 mm TL; females 310 mm TL

Western Australian biological stock: 1– 2 years; L50% 320 mm TL


L50% = length at which 50 percent of Tailor are mature; TL = total length


Figure 1: Distribution of reported commercial catch of Tailor in Australian waters, 2013 (calendar year)
Figure 1: Distribution of reported commercial catch of Tailor in Australian waters, 2013 (calendar year)



Table 3: Main features and statistics for Tailor fisheries in Australia, 2013 (calendar year)

Jurisdiction

Queensland

New South Wales

Victoria

Western Australia

Fishing methods

Commercial

Gillnet

Beach seine

Haul net

Tunnel nets

Rod and line

Purse seine

Dropline

Hand line

Powered reel

Recreationala

Rod and line

Gillnet

Haul nets

Indigenousb,c

Traditional apparatus

Rod and line

Management methods

Commercial

Limited entry

Size limits

Gear restrictions

Vessel restrictions

Total allowable catch

Total allowable effort

Seasonal or spatial closures

Spatial zoning

Trip limits

Recreationala

Bag limits

Possession limits

Size limits

Seasonal or spatial closures

Licensing

Limited entry (charter only)

Spatial zoning (charter only)

Passenger restrictions (charter only)

Indigenousa– e

Gear restrictions

Bag limits

Size limits

Seasonal or spatial closures

Section 37(1)(c1), Aboriginal cultural fishing authority

Active vessels

112 in ECIFFF

209 in EGF

35 in OHF

81 in OTLF

10 in CIF

10 in GLF

2 in OPSF

4 in PPBF

1 in EF

2 in GDSMF

13 in OA

7 in SBBSMNMF

19 in SCEMF

1 in WCDGDLIMF

5 in WCDSIMF

9 in WCEIMF

Catch

Commercial

37 t in ECIFFF

16 t in EGF

7 t in OHF

32 t in OTLF

<0.5 t in CIF

39 t in GLF

<0.5 t in OPSF

<0.1 t in PPBF

<0.5 t in EF

<0.5 t in GDSMF

1 t in OA

15 t in SBBSMNMF

2 t in SCEMF

<0.1 t in WCDGDLIMF

<0.1 t in WCDSIMF

13 t in WCEIMF

Recreational

140 t (201111)

253 t (200116)

Unknown

187 t (200116)

16 t (2011, boat-based catch only17; shore-based catches may account for 85% of recreational harvest4)

Indigenousf

Unknown

Unknown

None

Unknown

Markets

Domestic

Export


CIF = Corner Inlet Fishery (Victoria); ECIFFF = East Coast Inshore Fin Fish Fishery (Queensland); EF = Estuaries Fisheries (Condition) (Western Australia); EGF = Estuary General Fishery (New South Wales); GDSMF = Gascoyne Demersal Scalefish Managed Fishery (Western Australia); GLF = Gippsland Lakes Fishery (Victoria); OA = Open Access (Western Australia); OHF = Ocean Haul Fishery (New South Wales); OPSF = Ocean Purse Seine Fishery (Victoria); OTLF = Ocean Trap and Line Fishery (New South Wales); PPBF = Port Phillip Bay Fishery (Victoria); SBBSMNMF = Shark Bay Beach Seine and Mesh Net Managed Fishery (Western Australia); SCEMF = South Coast Estuarine Managed Fishery (Western Australia); WCDGDLIMF = West Coast Demersal Gillnet and Demersal Longline (Interim) Managed Fishery (Western Australia); WCDSIMF = West Coast Demersal Scalefish (Interim) Managed Fishery (Western Australia); WCEIMF = West Coast Estuarine (Interim) Managed Fishery (Western Australia)

a In Queensland, under the Fisheries Act 1994 (Qld), Indigenous fishers in Queensland are able to use prescribed traditional and noncommercial fishing apparatus in waters open to fishing. Size and possession limits, and seasonal closures do not apply to Indigenous fishers. Further exemptions to fishery regulations may be applied for through permits.

b In Victoria, regulations for managing recreational fishing are also applied to fishing activities by Indigenous people. Recognised Traditional Owners (groups that hold native title or have agreements under the Victorian Traditional Owner Settlement Act 2010) are exempt (subject to conditions) from the requirement to hold a recreational fishing licence, and can apply for permits under the Fisheries Act 1995 that authorise customary fishing (e.g. different catch and size limits, or equipment). The Indigenous category in Table 3 refers to customary fishing undertaken by recognised Traditional Owners. In 2012–13, there were no applications for customary fishing permits to access Tailor.

c
Subject to the defence that applies under section 211. of the Native Title Act 1993 (Cth), and the exemption from a requirement to hold a recreational fishing licence, the non-commercial take by indigenous fishers is covered by the same arrangements as that for recreational fishing.

d
The Aboriginal Fishing Interim Compliance Policy allows an Indigenous fisher in New South Wales to take in excess of a recreational bag limit in certain circumstances—for example, if they are doing so to provide fish to other community members who cannot harvest themselves.

e
The Aboriginal cultural fishing authority is the authority that Indigenous persons can apply to to take catches outside the recreational limits under the New South Wales Fisheries Management Act 1994 (NSW), section 37(1)(c1) (Aboriginal cultural fishing authority).

f
Tailor is a culturally significant species for Indigenous groups along the eastern seaboard. However, statewide estimates of harvest are unknown. In northern New South Wales, Tailor is a dominant component of the Indigenous catch19.


Figure 2: Commercial catch of Tailor in Australian waters, 2000 to 2013 (calendar years)
Figure 2: Commercial catch of Tailor in Australian waters, 2000 to 2013 (calendar years)



Effects of fishing on the marine environment
  • Commercial coastal-, river- and estuary-set gillnets have minimal impact on the environment and are quite selective in their harvest20. In general, gill-, seine- and haul-net methods used by commercial fishers in near-shore and estuarine waters are deployed in a targeted manner and result in minimal bycatch relative to the harvest of the target species. Mesh size regulations help to ensure that target species caught by these methods are within an appropriate size range. Fishers using tunnel nets in Queensland operate under the industry code of best practice to minimise their environmental impacts21.

  • Commercial gillnets can occasionally interact with threatened, endangered and protected species. The impact on populations of these species is unquantified. In most jurisdictions, commercial fishers are required to report all interactions with protected species.

  • Discarded fishing tackle from recreational fishers poses a risk to seabirds and marine life, which can become entangled in or injured by discarded gear22. Programs to safely dispose of unwanted fishing tackle are in place in south-east Queensland, New South Wales and Western Australia22.

  • Line-based fishing methods in near-shore and estuarine waters can result in the capture and release of a significant number of nontarget species and undersized fish. The rates of survival for released Tailor are high under some scenarios23,24. However, levels of discard mortality should be quantified for line-caught fish captured and released in surf breaks.


Environmental effects on Tailor
  • Near-shore habitats are important for this species, and Tailor populations are therefore vulnerable to any degradation in the quality of these habitats. Degradation may be from human causes (for example, pollution and habitat destruction) or natural causes (for example, floods), and has the potential to alter recruitment success of cohorts10.

  • Changes in coastal currents and water temperatures associated with climate change have the potential to alter fish behaviours (for example, spawning activity and migration) and to affect the dispersal of eggs and larvae, which may influence the subsequent recruitment of Tailor into fisheries3,25,26.



a Department of Agriculture, Fisheries and Forestry, Queensland
b Department of Environment and Primary Industries, Victoria
c Department of Fisheries, Western Australia
d Department of Primary Industries, New South Wales